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Journal of Entomology and Zoology Studies 2014; 2 (4): 35-41

ISSN 2320-7078 JEZS 2014; 2 (4): 35-41

© 2014 JEZS Received: 14-06-2014 Accepted: 23-06-2014

Srinath B S

Department of Zoology, Karnatak University Dharwad, India N Shivanna

Department of Applied Genetics, Karnatak University Dharwad, India

Correspondence:

N Shivanna

Department of Applied Genetics, Karnatak University Dharwad, India.

Seasonal variation in natural populations of Drosophila in Dharwad, India

Srinath B S, N Shivanna

ABSTRACT

Drosophila flies were collected in and around Dharwad district during different seasons of 2011 and 2012.

A total of 13853 individual flies comprising of 20 different species were collected by bottle trapping and net sweeping method. Maximum number (19) of species was recorded during monsoon 2012 and minimum number of species (5) during winter 2012 Statistical analysis revealed a positive correlation between abundance and average rainfall. No correlation was observed between abundance and temperature. The diversity of species was more during post-monsoon 2012 and less during winter 2012.

Their abundance cluster analysis revealed three clusters where D. malerkotliana, D. bipectinata, D. nasuta nasuta and Phorticella striata are predominant species. D. eugracilis, D. jambulina, D. rajasekari, D.

sulfurigaster neonasuta and D. ananassae are intermediate species whereas remaining 11 species are less dominant species.

Keywords: Biodiversity, Drosophila, Dharwad, seasonal variation, diversity indices, cluster analysis.

1. Introduction

Drosophila has been considered as a model system in the studies of genetics, evolution and ecology. There are about 65 genera classified under Drosophilidae family which is composed of more than 3,500 described species that occur in diverse ecosystems all over the world [15]. Some species are endemic to certain regions and few are cosmopolitan. These insects are highly sensitive to environmental variations which lead to fluctuation in their size of natural population.

Studies on the population structure and ecology of Drosophila species have provided important information in understanding their evolutionary process [2].

Studies on seasonal variation of Drosophila in different parts of the world have been carried out by earlier workers like Dobzhansky and Pavan [5] from Brazil; Paik [18] from South Korea and Wakahama [31] from Japan. Torres and Madi Ravazzi [29] have studied seasonal variation of Drosophila from Sao Paulo, Brazil. In India Parshad and Paika [19] have studied the effect of seasonal variation on Drosophila population from Punjab. Hegde et al. [11] have reviewed biodiversity, eco distributional pattern and seasonal variation of Drosophila species in South India. According to them out of 140 species in India, South India has 50 species. Most of the Drosophila diversity studies were concentrated on surrounding areas of Mysore in South Karnataka [25] and North Kanara district in northern part of Karnataka [17, 30] and the Western Ghats [22, 23, 24]. Most of the studies have revolved around altitudinal variation in relation to rainfall and temperature [7, 21, 8, 9, 10]. Recently Srinath and Shivanna [27] reported a variant of rare species D. daruma belonging to Polychaeta subgroup of the genus Drosophila from Kalghatgi forests of Western Ghats of South India. Seasonal variation studies on Drosophila of South India are fragmentary and poorly understood. In view of this, the present work has been undertaken to study the effect of seasonal variation on Drosophila species of Dharwad district.

2. Material and methods 2.1 Study area

Dharwad district is situated in the western sector of the northern half of Karnataka state. It lies between the latitudinal parallels of 15° 15' and 15° 35' North and longitudes of 75° 00' and 75°

20' East with an area of 4, 27,329 ha out of which 8.24% of land area is under forest. The district lies approximately about 800 meters above sea level, which is the reason for a moderate and healthy climate. The annual rainfall in the district ranges from 998.2 to 594.30 mm. Dharwad district is divided into 5 taluks Dharwad, Hubli, Kalghatgi, Kundagol and Navalgund.

Physiographical status of Dharwad falls within the macro region of Deccan Plateau.

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The district is classified into two prominent landscapes: the Dharwad and the black soil plains. The Dharwad landscape which features Sahyadrian region of the western belt of the district covers the Kalghatgi taluk. The landscape is marked by chain of low hill ranges. The landscape of black soil plains on this Sahyadrian region constitute a transitional belt where the hilly landscape of the west passes into the undulating plain of black soil. The forest land is concentrated in Kalghatgi taluk (28.39%), Dharwad (12.23%) and Hubli (2.75%) taluks. There is no forest land in Kundagol and Navalgund taluk. Monsoon deciduous forests are found in the Malnad zones which include Kalghatgi and Dharwad (Part of it) taluks [16]. On an average the western region of the district receives more rainfall than the eastern plains.

2.2 Collection and Sampling method

Flies were collected using both bottle trapping and net sweeping methods as mentioned by Hegde et al. [11]. Bottle trapping was done using 200 ml milk bottles filled with banana smash tied to trees at least two and half feet above the ground and left open for 24 to 48 hours. It was plugged with cotton before collection. The bottles were tied to trees where there was minimum exposure to sunlight especially during summer and monsoon. Care was taken to avoid rain entering the bottles as they get filled with water and flies collected from such bottles get stuck in the fruit media and are dead by the time they are brought to the laboratory. Net sweeping method was done by spreading the fruits on the ground under cool shaded areas. Sweeping was done after 24 to 48 hours of spreading.

Collection of flies was done during morning hours and the temperature was recorded.

A total of 8 bottles were tied per site for collection during each season. The trapped flies were brought to the laboratory and segregated according to their sex. Individual females were cultured in vials containing wheat cream agar medium [26]. The male flies were identified and recorded according to Hsu [12], Bock and Wheeler [3], Grimaldi [6] and Markow and O’ Grady [14]. Collection of flies was done from different localities such as the Western Ghat forests of Kalghatgi and Dharwad, fruit markets of Hubli and Dharwad, Mango and Guava orchards, residential areas and agricultural fields of all the 5 taluks. Drosophila flies were collected during different seasons of 2011 and 2012. The seasons were divided according to meteorological department of India as winter (January to February), summer (March to May), monsoon (June to September) and post-monsoon (October to December).

The rainfall data was obtained from the meteorological department of India (available online http://www.imd.gov.in).

The relationship between the abundance of individual species, average rainfall and temperature was analysed for different seasons

by means of the Spearman correlation coefficient (r) [29]. Diversity of the flies during different seasons and of different taluks was calculated using Simpson Index (1-D), Shannon index (H) and Equitability index (J) using PAST 3.X software [15, 9]. Simpson Index was calculated to analyze the probability that two individuals randomly selected from a sample belong to the same species.

Formula to calculate Simpson index is D = 1- ∑ni (ni-1)/N (N-1) where ni = the total number of organisms of particular species; N=

the total number of organisms of all population. Shannon index was calculated using the formula H' = -ln ∑pi ln pi where pi = proportion of individuals belonging to the same species in a given sample. The equitability index was also calculated using the formula J|= - ln ∑ pi

ln pi / ln N. This is the Shannon Weiner diversity Index divided by ln N. This index measures the uniformity or equity of the species distribution [13].

SPSS 16.0 statistical package was used to determine the level of similarity of the 20 species of Drosophilids obtained and hierarchical cluster analysis (Euclidean distances, Ward’s method) was used to construct a single linkage dendrogram. Cluster analysis is a technique used to classify cases into groups that are relatively homogeneous within themselves and heterogeneous between each other.

3. Results

Table 1 shows the number of Drosophila species collected in and around Dharwad district during different seasons of 2011 and 2012.

It revealed that 13853 individual flies were collected consisting of a total of 20 species; among which, 11 species belonged to subgenus Sophophora, 4 belonged to subgenus Drosophila, and 2 belonged to genus Scaptodrosophila, while one species each belonged to genus Zaprionus and Phorticella respectively.

Maximum flies were obtained during monsoon 2012 whereas minimum flies were obtained during winter 2012. D. malerkotliana and D. bipectinata were found to be abundant during monsoon, followed by D. n. nasuta and P. striata. During summer, P. striata was abundantly found. During post-monsoon, D. n. nasuta was found dominant followed by D. malerkotliana and D. bipectinata.

During winter D. ananassae was dominant species. D.

melanogaster, D. ananassae, D. malerkotliana and P. striata were found in all the seasons. Rare species such as D. punjabiensis, D.

bhagamandalensis, and D. daruma were found only during monsoon and post-monsoon season whereas D. latifshahi was found during summer 2012 season. The abundance of Drosophila population varied for different seasons. Drosophila population size was found to be maximum during monsoon and minimum during winter.

Table 1: Seasonal variation of Drosophila in Dharwad District collected during 2011-12 season

Species Winter

2011

Summer 2011

Monsoon 2011

Post- monsoon

2011

Winter 2012

Summer 2012

Monsoon 2012

Post- monsoon

2012

Total Genus Drosophila

Subgenus Sophophora melanogaster subgroup

Drosophila melanogaster 12 15 65 11 14 8 82 24 231 ananassae subgroup

D. ananassae D. malerkotliana

D. bipectinata

121 18

3

273 64 53

206 1186 1314

41 196 167

86 8 --

211 46 35

148 1405 1398

25 155 117

1111 3078 3087

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suzukii subgroup

D. rajasekarii -- 42 187 30 -- 17 234 10 520 eugracilis subgroup

D. eugracilis -- 2 82 136 -- 7 67 112 406 montium subgroup

D. kikkawai D. jambulina D. punjabiensis D. bhagamandalensis

6 -- -- --

7 12

-- --

18 114

2 4

25 65 -- 5

-- -- -- --

3 16

-- --

34 178

3 3

15 34 -- 4

108 419 5 16 takahashii subgroup

D. takahashii -- -- 5 -- -- -- 6 2 13 Subgenus Drosophila

immigrans group D. nasuta D. neonasuta

20 --

39 3

447 289

152 48

12 --

76 14

762 133

178 88

1686 575 repleta group

D. repleta 8 13 17 2 -- 21 21 13 95 Polychaeta group

D. daruma*

D. latifshahi*

--

-- --

-- --

-- --

-- --

-- --

3 3

-- --

-- 3

3 Genus Scaptodrosophila

Scaptodrosophila nigra S. krishnamurthyii

--

-- 12

4 34

7 --

-- --

-- 4

15 24

4 --

-- 74

30 Genus Zaprionus

Zaprionus bogoriensis 18 10 48 2 -- 13 73 13 177 Genus Phorticella

Phorticella striata 13 237 776 78 9 337 681 85 2216

Total 219 786 4801 958 129 826 5259 875 13853

Average rainfall (in mm) Average temperature (0C)

3.85 23.5

37.4 27.5

112 24

56.9 25

0.0 23.5

22.8 27

70.9 24.5

40.6 26.5 Source: Classification according to Hsu (1949); Bock and Wheeler (1972); Grimaldi (1990) and Markow and O’ Grady (2006)

* Rare species collected for first time from South India

Figure 1 revealed that there was a positive correlation between average rainfall and abundance of the species (r = 0.952).

Fig 1: Correlation between average rainfall and population abundance of Drosophila during 2011-12 seasons.

The correlation coefficient analysis for individual species revealed that out of 20 species about 12 species showed positive correlation with rainfall (Table 2).

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Table 2: Correlation coefficient (r) value of individual species of Drosophila against average rainfall for 2011-12 season

S. No. Species r value

1 Drosophila melanogaster 0.595

2 D. ananassae 0.048

3 D. malerkotliana 0.976**

4 D. bipectinata 0.976**

5 D. rajasekari 0.850**

6 D. eugracilis 0.778*

7 D. kikkawai 0.905**

8 D. jambulina 0.946**

9 D. punjabiensis 0.733*

10 D. bhagamandalensis 0.779*

11 D. takahashii 0.764*

12 D. nasuta 0.929**

13 D.s. neonasuta 0.946**

14 D. repleta 0.494

15 D. daruma 0.412

16 D. latifshahi -0.247

17 Scaptodrosophila nigra 0.634

18 S. krishnamurthyii 0.345

19 Zaprionus bogoriensis 0.551

20 Phorticella striata 0.762*

* Significant at 0.05 level, ** Significant at 0.01level

The correlation coefficient between temperature and abundance of species was not found significant (Fig. 2)

Fig 2: Correlation between average temperature and population abundance of Drosophila during 2011-12 seasons The Simpson index of diversity and Shannon index calculated for

different seasons revealed that post-monsoon 2012 were more diverse whereas winter 2012 was less diverse. Post-monsoon 2011

had more values for equitability index whereas summer 2012 revealed less values (Table 3).

Table 3: Diversity indices values calculated for Seasonal variation of Drosophila during 2011-12 Seasons No. of species recorded Simpson index Shannon index Equitability index

Winter 2011 9 0.6641 1.562 0.7109

Summer 2011 15 0.7706 1.852 0.684

Monsoon 2011 18 0.8155 2.011 0.6957

Post-monsoon 2011 14 0.865 2.178 0.8253

Winter 2012 5 0.6454 1.09 0.6775

Summer 2012 16 0.7524 1.838 0.6628

Monsoon 2012 19 0.815 1.981 0.6728

Post-monsoon 2012 15 0.8695 2.231 0.8239

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Cluster analysis on the basis of abundance of different species showed two main clusters (Fig. 3). First cluster consists of about 16 species whereas second cluster consists of 4species. First cluster is further divided into 2 sub clusters consisting of 11 and 5 species respectively. Out of 11 species 5 belong to the subgenus Sophophora whereas 3 species belong to subgenus Drosophila, 2 species belong to Genus Scaptodrosophila and one species belongs

to Genus Zaprionus. Out of 5 species present in the second sub cluster 4 belong to subgenus Sophophora while one species belong to subgenus Drosophila. The second cluster also consists of two sub clusters consisting of sympatric species D. malerkotliana and D. bipectinata belonging to subgenus Sophophora. D. n. nasuta belonging to subgenus Drosophila and P. striata belonging to Genus Phorticella are in the second sub cluster.

Fig 3: Cluster analysis of Drosophila species 4. Discussion

There is an effect of seasons on the population of Drosophila of Dharwad. They were more abundant during monsoon, less abundant during winter and moderate during summer and post- monsoon season. Few species which were found during monsoon season were rare and endemic. During monsoon, D. bipectinata, D.

malerkotliana, D. n. nasuta and P. striata were more dominant than other species. During post-monsoon and winter seasons, the population of these species decreased but they maintained their dominancy compared to other species. Present study agrees with the reports of Prakash and Reddy [22, 23]; Guruprasad et al. [8] and Achumi et al. [1] where majority of species collected belonged to melanogaster species group of the subgenus Sophophora and immigrans species group of the subgenus Drosophila indicating their sympatric association and ecological dominance [11]. During the months of summer, P. striata emerged as most successful species in summer as it is the mango fruit harvesting season in this area (Table 1). It is also reported that P. striata species is dependent on mango fruiting season during summer and decreases its abundance during other seasons. This fruit provides an excellent source of feeding and breeding site for the Drosophilids [28].

Fluctuations in tropical population sizes of Drosophila during different seasons are due to variations in the environmental factors such as rainfall, temperature and humidity [19]. Present study revealed that fluctuation in population densities of various species of Drosophila can be attributed to rainfall with more number of individual flies collected in monsoon compared to other seasons

and the size of the population decreases slowly by post-monsoon and reaches its lowest during dry winter season and again increases during summer. Torres and Madi – Ravazzi [29] reported that there is a positive correlation between population abundance and rainfall of three populations of Brazil. They have reported that populations of D. sturtevanti and D. malerkotliana were strongly influenced by rainfall. During the dry season, the number of individuals of both species was significantly reduced. Present study shows positive correlation between total abundance of species and rainfall (Fig. 1) and also among 12 individual species. D. melanogaster and D.

ananassae are considered as cosmopolitan species [20]. But these species showed no positive correlation with rainfall. Sympatric species D. bipectinata and D. malerkotliana coexisted during all the seasons in equal numbers and hence, justifies their adaptability to share the same habitat and maintain a successful reproductive isolation (Table 2).

Dobzhansky and Pavan [5] showed that rainfall has greater influence on the abundance of species than temperature. An increase in rainfall has direct influence on flowering and fruiting of plants, thus increasing the number of oviposition and feeding sites for the species [4]. Torres and Madi – Ravazzi [29] have reported no correlation between the total number of individuals captured and temperature among two out of three populations of Brazil. Present study also revealed that temperature has no relation with abundance of Drosophila population (Fig. 2).

Species richness alone has no effect on diversity indices [29]. Achumi et al. [1] have calculated Simpson’s index during the study

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of seasonal variation of Drosophila from Mount Japfu. Their results revealed that species richness has no significant effect on diversity. Similar results were reported by Guruprasad et al. [8]

where a lower altitude region (680 m) with less number of species (18) was more diverse than higher altitude region (980 m) with more number of species (19). The Simpsons Index of diversity (1- D), Shannon Index revealed a greater diversity in the post-monsoon 2012 season even though monsoon 2012 season recorded maximum number of species (19). Minimum diversity was found in winter 2012 (Table 3). This may be more easily understood if we observe the quantity and dominance of each species collected during different seasons, Most of the flies collected during monsoon seasons were concentrated in just two species, D.

malerkotliana and D. bipectinata, which together represent 52.7%

of the whole sample collected. Whereas in post-monsoon season their population was stable and evenness maintained. Simpson’s Index is heavily dependent towards evenness and most abundant species in the sample and it is less sensitive to the species richness whereas Shannon index takes into account both species richness and abundance [13].

Eco-distributional analysis of Drosophila revealed that the distributional pattern of species or related group of species is uneven [1, 8]. Cluster analysis revealed that there are 2 major clusters of species, first cluster consisting of rare, endemic and cosmopolitan species which were found in less number where as the other sub cluster consists of intermediate species whose abundance is in between first sub cluster and second cluster. In the first cluster out of 16 species, 9 belonged to subgenus Sophophora which are morphologically related to each other thus indicating the coexistence of species having similar ecological preferences.

Second cluster is further divided into two sub clusters where one sub cluster consists of dominant sympatric species D.

malerkotliana and D. bipectinata. The other sub cluster consists of D. n. nasuta and P. striata which were also dominantly found species (Fig. 3).

5. Conclusion

The study revealed that Dharwad District is rich in Drosophila fauna endowed with rare and endemic species and further studies on species specific habitat/ microhabitat preferences will be very much helpful in understanding their ecological pattern and speciation.

6. Acknowledgement

The authors are thankful to the chairperson, Dept. of Zoology, Karnatak University, Dharwad for providing necessary facilities.

S.B.S. is thankful to UGC for award of Rajiv Gandhi National Fellowship and N.S to UGC MRP F. NO. 37/-241/2009 (SR) for financial assistance

7. References

1. Achumi B, Hegde SN, Lal P, Yenisetti SC. Altitudinal and seasonal variation in Drosophila species on mount Japfu of Nagaland, a sub-Himalayan hilly state of India. Journal of Insect Science 2013; 13:117.

http://www.insectscience.org/ 30 June, 2014.

2. Bizzo N, Sene F. Studies on the natural populations of Drosophila from Perulibe (SP) Brazil (Diptera:

Drosophilidae). Revista Brasileira de Biologia, 1982;

42:539–544.

3. Bock IR, Wheeler MR. The Drosophila melanogaster species group. University of Texas Publications, 1972;

7213:1–102.

4. Brncic DM, Budnik M, Guines R. An analysis of a

Drosophilidae community in Central Chile during a three years period. Journal of Zoological Systematics and Evolutionary Research, 1985; 23:90–100.

5. Dobzhansky T, Pavan C. Local and seasonal variations in relative frequencies of species of Drosophila in Brazil, 1950; 19(1):1–14.

6. Grimaldi DA. A phylogenetic revised classification of genera in the Drosophilidae (Diptera). Bulletin of the American Museum of Natural History, 1990; 197:1–139.

7. Guruprasad BR, Hegde SN. Altitudinal and Seasonal fluctuation of Drosophila fauna of Chamundi hill.

Drosophila Information Service 2006; 89:10–11.

8. Guruprasad BR, Hegde SN, Krishna MS. Seasonal and altitudinal changes in population density of 20 species of Drosophila in Chamundi hill. Journal of Insect Science, 2010; 10:123.

http://www.insectscience.org/10.123.

9. Guruprasad BR, Pathak P, Hegde SN. Assessment of Drosophila diversity during monsoon season. Journal of Entomology and Nematology 2011; 3:54–57.

10. Guruprasad BR, Pathak P. Studies on Drosophila biodiversity of Harangi Forest: Coorg District, Karnataka.

Drosophila Information Service, 2011; 94:93–95.

11. Hegde SN, Vasudev V, Krishna MS. Trends in Wildlife Biodiversity Conservation and Management. Ed, BB Hosetti, M Venkateswarulu, Daya Publishing House, New Delhi, 2001, 55-71.

12. Hsu TC. Studies in the Genetics of Drosophila VI, Ed, JT Patterson, 4920, University of Texas Publications, USA, 1949, 80-142.

13. Magurran A. Measuring Biological Diversity. Blackwell Science Publishing Ltd. 2004, 248.

14. Markow TA, Grady Patrick O’. Drosophila, A guide to species identification and use. Academic Press, London, 2006, 247.

15. Mateus RP, Buschini MLT, Sene FM. The Drosophila community in xerophytic vegetations of the upper Parana- Paraguay River Basinet. Brazilian Journal of Biology 2006; 66(2B):719-729.

16. Motebennur SS. Land-Use under jowar Sown area, production and per hectare yield of Dharwad District of Karnataka: A Geographical Analysis. Global Research Analysis 2012; 1(5):74-76.

17. Nagaraj HJ, Krishnamurthy NB. Drosophila fauna of Dandeli and Ambikanagar. Drosophila Information Service 1980; 55:114.

18. Paik YK. Seasonal changes in Drosophila populations in two adjacent areas of Korea. Drosophila Information Service 1957; 31:151-153.

19. Parshad R, Paika IJ. Drosophilid survey of India II.

Taxonomy and Cytology of the subgenus Sophophora (Drosophilidae), Research Bulletin of the Punjab University 1964; 15:225-252.

20. Parsons PA. The population biology of Australian Drosophila. Annual Review of Ecology and Systematics 1979; 10:229-245.

21. Prakash A, Ramachandra NB. Distribution of Drosophila flies in eight different altitudes of three districts of Karnataka, India. Drosophila Information Service 2008;

91:82-87.

22. Prakash HS, Reddy GS. Drosophila fauna of Bababudangiri and Kemmannugundi Hill ranges (Western Ghats). Entomon 1978; 3(1):85-90.

23. Prakash HS, Reddy GS. Drosophila fauna of Sahyadri

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Hills (Western Ghats) with description of a new species.

Proc. Indian Academy of Sciences 1979; 88(1):65–72.

24. Prakash HS, Reddy GS. Drosophila fauna of Nagarhole, South India, including description of a new species (Diptera: Drosophilidae). Proc Indian Academy of Sciences 1980; 89(3):235–241.

25. Reddy GS, Krishnamurthy NB. Systematics and Distribution of Drosophila fauna of South India. Journal of University of. Mysore 1974; 26(B):54–64.

26. Shivanna N, Siddalingamurthy GS, Ramesh SR. Larval pupation site preference and its relationship to the glue proteins in few species of Drosophila, Genome 1996;

39:105–111.

27. Srinath BS, Shivanna N. Note on a new variant of Drosophila daruma Okada (Diptera: Drosophilidae) from Kalghatgi forest range, Dharwad, of Western Ghats, Biosystematica 2012; 6(1):39–42.

28. Srinath BS, Shivanna N. Fluctuation of Phorticella striata in mango plantations of Dharwad District. Drosophila Information Service 2013; 96:61–64.

29. Torres FR, Madi-Ravazzi L. Seasonal variation in natural populations of Drosophila spp. (Diptera) in two woodlands in the State of São Paulo, Brazil. Iheringia.

Série Zoologia Porto Alegre 2006; 96(4):437–444.

30. Vasudev V, Nagaraj HJ, Nagabhushana, Hegde SN.

Altitudinal and seasonal distribution of Drosophila species in North Kanara region of Western Ghats.

Entomon 2001; 26(special issue):326–331.

31. Wakahama KI. Notes on the seasonal activity of Drosophila observed in the Rakuzan park, Matsue city.

Bulletin of Shimane University (Natural science) 1961;

10:90–95.

References

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